In addition to the provisions of Section P3009
, systems for flushing of water closets
and urinals shall comply with Section P3009.13
and systems for subsurface landscape irrigation shall comply with Section P3009.14
. Except as provided for in Section P3009
, all systems shall comply with the provisions of the other sections of this code.
Only connections in accordance with Section 3009.13.1 shall be made between a gray water
recycling system and a potable water
recycling systems shall receive only the waste
discharge of bathtubs, showers, lavatories, clothes washers or laundry trays.
shall be collected in an approved reservoir constructed of durable, nonabsorbent and corrosion-resistant materials. The reservoir shall be a closed and gas-tight vessel. Access openings shall be provided to allow inspection and cleaning of the reservoir interior.
entering the reservoir shall pass through an approved filter such as a media, sand or diatomaceous earth filter.
A full-open valve shall be installed downstream of the last fixture connection to the gray water
discharge pipe before entering the required filter.
The collection reservoir shall be equipped with an overflow pipe having the same or larger diameter
as the influent pipe for the gray water
. The overflow pipe shall be trapped and shall be indirectly connected to the sanitary drainage system.
shall be located at the lowest point of the collection reservoir and shall be indirectly connected to the sanitary drainage system. The drain
shall be the same diameter
as the overflow pipe required in Section P3009.10
The reservoir shall be provided with a vent
sized in accordance with Chapter 31
and based on the diameter
of the reservoir influent pipe.
The holding capacity of the reservoir shall be a minimum of twice the volume of water required to meet the daily flushing requirements of the fixtures supplied with gray water
, but not less than 50 gallons (189 L). The reservoir shall be sized to limit the retention time of gray water
to a maximum of 72 hours.
shall be disinfected by an approved method that employs one or more disinfectants such as chlorine, iodine or ozone that are recommended for use with the pipes, fittings and equipment
by the manufacturer of the pipes, fittings and equipment
shall be supplied as a source of makeup water for the gray water
system. The potable water
supply shall be protected against backflow in accordance with Section P2902
. There shall be a full-open valve located on the makeup water supply line to the collection reservoir.
The gray water
shall be dyed blue or green with a food-grade
vegetable dye before such water is supplied to the fixtures.
Distribution piping shall conform to one of the standards listed in Table P2905.4
Distribution piping and reservoirs shall be identified as containing nonpotable water. Piping identification shall be in accordance with Section P2901.1
Reservoirs shall be sized to limit the retention time of gray water
to a maximum of 24 hours.
The reservoir shall be identified as containing nonpotable water.
A check valve and a full-open valve located on the discharge side of the check valve shall be installed on the effluent pipe of the collection reservoir.
Makeup water shall not be required for subsurface landscape irrigation systems. Where makeup water is provided, the installation shall be in accordance with Section 3009.13.3.
Disinfection shall not be required for gray water
used or subsurface landscape irrigation systems.
used for subsurface landscape irrigation systems shall not be required to be dyed.
The system shall be sized in accordance with the gallons-per-day-per-occupant number based on the type of fixtures connected to the gray water
system. The discharge shall be calculated by the following equation:
Number of occupants shall be determined by the actual number of occupants, but not less than two occupants for one bedroom and one occupant for each additional bedroom.
|B||=||Estimated flow demands for each occupant:|
Residential—25 gallons per day (94.6 lpd) per occupant for showers, bathtubs and lavatories and 15 gallons per day (56.7 lpd) per occupant for clothes washers or laundry trays.
|C||=||Estimated gray water discharge based on the total number of occupants.|
The permeability of the soil in the proposed absorption system shall be determined by percolation tests or permeability evaluation.
At least three percolation tests in each system area shall be conducted. The holes shall be spaced uniformly in relation to the bottom depth of the proposed absorption system. More percolation tests shall be made where necessary, depending on system design.
The test hole shall be dug or bored. The test hole shall have vertical sides and a horizontal dimension of 4 inches to 8 inches (102 mm to 203 mm). The bottom and sides of the hole shall be scratched with a sharp-pointed instrument to expose the natural soil. All loose material shall be removed from the hole and the bottom shall be covered with 2 inches (51 mm) of gravel or coarse sand.
The hole shall be filled with clear water to a minimum of 12 inches (305 mm) above the bottom of the hole for tests in sandy soils. The time for this amount of water to seep away shall be determined, and this procedure shall be repeated if the water from the second filling of the hole seeps away in 10 minutes or less. The test shall proceed as follows: Water shall be added to a point not more than 6 inches (152 mm) above the gravel or coarse sand. Thereupon, from a fixed reference point, water levels shall be measured at 10-minute intervals for a period of 1 hour. Where 6 inches (152 mm) of water seeps away in less than 10 minutes, a shorter interval between measurements shall be used, but in no case shall the water depth exceed 6 inches (152 mm). Where 6 inches (152 mm) of water seeps away in less than 2 minutes, the test shall be stopped and a rate of less than 3 minutes per inch (7.2 s/mm) shall be reported. The final water level drop shall be used to calculate the percolation rate. Soils not meeting the above requirements shall be tested in accordance with Section 3009.14.7.1.3.
The hole shall be filled with clear water, and a minimum water depth of 12 inches (305 mm) shall be maintained above the bottom of the hole for a 4-hour period by refilling whenever necessary or by use of an automatic siphon. Water remaining in the hole after 4 hours shall not be removed. Thereafter, the soil shall be allowed to swell not less than 16 hours or more than 30 hours. Immediately after the soil swelling period, the measurements for determining the percolation rate shall be made as follows: Any soil sloughed into the hole shall be removed and the water level shall be adjusted to 6 inches (152 mm) above the gravel or coarse sand. Thereupon, from a fixed reference point, the water level shall be measured at 30-minute intervals for a period of 4 hours, unless two successive water level drops do not vary by more than 1/16 inch (1.59 mm). At least three water level drops shall be observed and recorded. The hole shall be filled with clear water to a point not more than 6 inches (152 mm) above the gravel or coarse sand whenever it becomes nearly empty. Adjustments of the water level shall not be made during the three measurement periods except to the limits of the last measured water level drop. When the first 6 inches (152 mm) of water seeps away in less than 30 minutes, the time interval between measurements shall be 10 minutes and the test run for 1 hour. The water depth shall not exceed 5 inches (127 mm) at any time during the measurement period. The drop that occurs during the final measurement period shall be used in calculating the percolation rate.
Mechanical percolation test equipment
shall be of an approved type.
Soil shall be evaluated for estimated percolation based on structure and texture in accordance with accepted soil evaluation practices. Borings shall be made in accordance with Section P3009.14.7.1
for evaluating the soil.
The surface grade
of all soil absorption systems shall be located at a point lower than the surface grade
of any water well or reservoir on the same or adjoining lot. Where this is not possible, the site shall be located so that surface water drainage from the site is not directed toward a well or reservoir. The soil absorption system shall be located with a minimum horizontal distance between various elements as indicated in Table P3009.14.8
. Private sewage
disposal systems in compacted areas, such as parking lots and driveways, are prohibited. Surface water shall be diverted away from any soil absorption site on the same or neighboring lots.
LOCATION OF GRAY WATER SYSTEM
|ELEMENT||MINIMUM HORIZONTAL DISTANCE|
|HOLDING TANK |
|Property line adjoining private property||5||5|
|Public water main||10||10|
|Streams and lakes||50||50|
For SI: 1 foot = 304.8 mm.
The total absorption area required shall be computed from the estimated daily gray water
discharge and the design-loading rate based on the percolation rate for the site. The required absorption area equals the estimated gray water
discharge divided by the design-loading rate from Table P3009.14.9.1
DESIGN LOADING RATE
|PERCOLATION RATE |
(minutes per inch)
|DESIGN LOADING FACTOR |
(gallons per square foot per day)
|0 to less than 10||1.2|
|10 to less than 30||0.8|
|30 to less than 45||0.72|
|45 to 60||0.4|
For SI: 1 minute per inch = min/25.4 mm,
1 gallon per square foot = 40.7 L/m2.
Seepage trench excavations shall be a minimum of 1 foot (304 mm) to a maximum of 5 feet (1524 mm) wide. Trench excavations shall be spaced a minimum of 2 feet (610 mm) apart. The soil absorption area of a seepage trench shall be computed by using the bottom of the trench area (width) multiplied by the length of pipe. Individual seepage trenches shall be a maximum of 100 feet (30 480 mm) in developed length
Seepage bed excavations shall be a minimum of 5 feet (1524 mm) wide and have more than one distribution pipe. The absorption area of a seepage bed shall be computed by using the bottom of the trench area. Distribution piping in a seepage bed shall be uniformly spaced a maximum of 5 feet (1524 mm) and a minimum of 3 feet (914 mm) apart, and a maximum of 3
feet (914 mm) and a minimum of 1 foot (305 mm) from the sidewall or headwall.
The bottom of a trench or bed excavation shall be level. Seepage trenches or beds shall not be excavated where the soil is so wet that such material rolled between the hands forms a soil wire. All smeared or compacted soil surfaces in the sidewalls or bottom of seepage trench or bed excavations shall be scarified to the depth of smearing or compaction and the loose material removed. Where rain falls on an open excavation, the soil shall be left until sufficiently dry so a soil wire will not form when soil from the excavation bottom is rolled between the hands. The bottom area shall then be scarified and loose material removed.
A minimum of 6 inches (152 mm) of aggregate ranging in size from 1/2 inch to 21/2 inches (12.7 mm to 64 mm) shall be laid into the trench below the distribution piping elevation. The aggregate shall be evenly distributed a minimum of 2 inches (51 mm) over the top of the distribution pipe. The aggregate shall be covered with approved synthetic materials or 9 inches (229 mm) of uncompacted marsh hay or straw. Building paper shall not be used to cover the aggregate. A minimum of 9 inches (229 mm) of soil backfill shall be provided above the covering.